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Evaluation of a wind tunnel for measurement of odour emission from area sources.

机译:评估风洞以测量区域源发出的气味。

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摘要

The wind tunnel method is commonly used for sampling odour from area emission sources. The performance of a wind tunnel in odour sampling is influenced by its design and aerodynamic characteristics. A laboratory study was conducted to evaluate the performance of a wind tunnel in odour sampling from a liquid emission surface. The wind tunnel evaluated consisted of an inlet bucket, a carbon filter, a fan, a PVC duct, an expansion section, a flux hood, a contraction section, a mixing chamber and two gas sampling ports. A perforated baffle was installed between the hood and the contraction section to facilitate creating uniform air flow in the hood. N-butanol solutions of various concentrations were used to simulate odour emission from liquid surfaces. An identical tunnel hood, which is 800 mm long, 400 mm wide and 250 mm high, was built with Plexiglas in order to perform velocity measurement and visual smoke testing. A total of 24 sampling ports were drilled for velocity measurement at the top surface of the hood at 200 mm, 400 mm and 600 mm of the hood length, 8 ports each length. The air velocity profiles were measured at bulk velocities of 0.20, 0.24, 0.30 and 0.38 m/s in the wind tunnel by inserting a hot wire anemometer at five different depth of each sampling port. The velocity profiles were deduced from the average velocities in the vertical and horizontal direction at 0.20, 0.24, 0.30 and 0.38 m/s bulk velocities. Smoke tests were conducted to visualize the air flow patterns in the tunnel. The flow pattern was recorded by a high speed motion camera and reviewed frame by frame. Computational Fluid Dynamics (CFD) modeling was performed to verify the flow patterns. The odour pick-up (recovery) rate was calculated from the mass balance of n-butanol in the solution and in the gas. N-butanol solution concentration was measured by using a spectrophotometer together with an ethanol UV testing kit and the gaseous concentration at the exit of the wind tunnel was measured by using a photo ionization detector.; The measured velocity profiles exhibited a substantial degree of non-uniformity in the hood while the velocity at the central hood was relatively uniform. The lower the bulk velocity, the less the velocity variation. The air flow inside the hood was turbulent, confirmed by the calculated Reynolds Number of 4820 at the lowest bulk velocity of 0.20 m/s in the experiment. The pick-up rate ranged from 37% to 56% using the current sampling system. Therefore, caution should be exercised when interpreting and using odour emission data obtained with wind tunnels. Even similar wind tunnel designs could yield different performance results. The odour emission rate measured by the wind tunnel increased with the bulk air velocity in the tunnel and the relationship could be described by the power function.; Keywords. Odour emission, Wind tunnel, Velocity profile, Pick-up rate
机译:风洞法通常用于采样区域排放源的气味。风洞在气味采样中的性能受其设计和空气动力学特性的影响。进行了一项实验室研究,以评估风洞在从液体排放表面进行气味采样中的性能。评估的风洞包括进气口,碳过滤器,风扇,PVC管,膨胀段,通气罩,收缩段,混合室和两个气体采样口。通风罩和收缩部分之间安装了多孔挡板,以方便在通风罩中产生均匀的气流。使用各种浓度的正丁醇溶液模拟从液体表面发出的气味。为了进行速度测量和目视烟雾测试,使用有机玻璃建造了一个相同的隧道罩,该罩长800毫米,宽400毫米,高250毫米。在引擎盖顶面以200 mm,400 mm和600 mm的引擎盖长度钻了24个采样口用于速度测量,每个长度8个端口。通过在每个采​​样端口的五个不同深度处插入热丝风速计,在风洞中以0.20、0.24、0.30和0.38 m / s的总速度测量空气流速曲线。从垂直速度和水平方向的平均速度推导出速度曲线,分别为0.20、0.24、0.30和0.38 m / s。进行了烟雾测试以可视化隧道中的气流模式。用高速运动摄像机记录流型并逐帧检查。执行计算流体动力学(CFD)建模以验证流型。由溶液和气体中正丁醇的质量平衡计算气味吸收(回收)率。用分光光度计和乙醇紫外检测试剂盒测定正丁醇溶液的浓度,用光电离检测器测定风洞出口处的气体浓度。测得的速度分布在通风橱中显示出很大程度的不均匀,而中央通风橱的速度则相对均匀。整体速度越低,速度变化越小。发动机罩内的气流湍流,在实验中以最低体积速度0.20 m / s计算得出的雷诺数4820证实了这一点。使用当前的采样系统,拾取率从37%到56%不等。因此,在解释和使用通过风洞获得的气味排放数据时应格外小心。即使是类似的风洞设计,也会产生不同的性能结果。风洞测得的臭味释放率随风洞中的风速增加而增加,其关系可用幂函数来描述。关键字。气味排放,风洞,速度分布,吸收率

著录项

  • 作者

    Wu, Wenyue.;

  • 作者单位

    University of Manitoba (Canada).;

  • 授予单位 University of Manitoba (Canada).;
  • 学科 Environmental Sciences.
  • 学位 M.Sc.
  • 年度 2007
  • 页码 72 p.
  • 总页数 72
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 环境科学基础理论;
  • 关键词

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